Forest Operations and Badger Setts Forestry Practice Guide 9
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Forestry Practice Guide 9 Forest Operations and Badger Setts Forestry Practice Guide 9 Forest Operations and Badger Setts C ONTENTS Page INTRODUCTION 1 BADGER SETTS & THE LAW 2 MANAGEMENT GUIDELINES 4 General 4 Locating and Recording Setts 4 Identifying Setts in Current Use by Badgers 6 Timing of Forest Operations 8 Protection Zones Around Setts 8 Thinning 9 Clear Felling 10 Ground Preparation and Tree Planting 10 Civil Engineering 11 Recreational Activities 12 A PPLYING FOR A LICENCE 14 Who Should Apply? 14 When to Apply for a Licence 15 F URTHER READING AND ADVICE 16 iii FOREST OPERATIONS AND BADGER SETTS C ONTENTS (CONTD) ACKNOWLEDGEMENTS 17 ANNEX A 18 PROTECTION OF BADGERS ACT 1992 18 List of Sections Which Create Offences & Exceptions 18 A NNEX B 21 LICENSING AUTHORITIES 21 1. Forestry Operations 21 2. Development & Other Activities 24 iv I NTRODUCTION adgers are protected under the Protection of Badgers Act 1992. BIt is an offence to damage or obstruct a badger sett which shows signs of current use by badgers, or to disturb a badger within a sett. Forest operations such as tree felling, timber extraction and mechanical cultivation are potential sources of damage or disturbance to badger setts. The Forestry Commission has consulted the Ministry of Agriculture, Fisheries and Food (MAFF), Scottish Office Agriculture and Fisheries Department (SOAFD), Welsh Office Agriculture Department (WOAD), Agricultural Development Advisory Service (ADAS), English Nature (EN), Scottish Natural Heritage (SNH) and the Countryside Council for Wales (CCW) in preparing this guide. It gives advice on: · The law concerning forest operations and badger setts. · Practices which will minimise damage and disturbance to badger setts from forestry. · When and where to obtain further advice. This guide concentrates upon safeguarding setts and badgers within setts. It is not intended to provide comprehensive advice on the wider aspects of managing forests for the benefit of badgers although it includes some measures which go beyond what is strictly necessary to avoid an offence under the 1992 Act, in order to minimise disturbance to badgers beyond the immediate vicinity of the sett. Neil McReddie 1 FOREST OPERATIONS AND BADGER SETTS B ADGER SETTS AND THE LAW he Protection of Badgers Act 1992 consolidated earlier Tlegislation, namely the Badgers Act 1973, as amended, The Badgers Act 1991 and The Badgers (Further Protection) Act 1991. The 1992 Act created a number of offences. For example, except if permitted by or under the Act, it is an offence to wilfully kill, injure or take a badger; to interfere with a sett by damaging or obstructing it or by disturbing a badger when it is occupying a badger sett, with intent or recklessly. A sett is defined in the Act as any structure or place which displays signs indicating current use by a badger, and can be interpreted as including underground holes and other places of shelter occasionally used by badgers, such as sheds, concrete pipes or culverts etc. There are also a number of statutory defences in the 1992 Act. For example, a defence to damaging a badger sett would be that the damage was the incidental result of a lawful operation and could not reasonably have been avoided. This is not an exhaustive list of the offences and exceptions in the 1992 Act. Annex A lists the relevant sections of the Act. For further detail readers should consult the Act itself. The Act also contains provisions to permit (by means of a licence) certain activities which would otherwise be prohibited under the Act. The licensing authorities responsible for the issue of licences under the 1992 Act are the agricultural departments and the statutory nature conservation agencies (English Nature (EN), referred to as the Nature Conservancy Council for England in the Act, Scottish Natural Heritage (SNH) and the Countryside Council for Wales (CCW). Licences for forestry operations are the responsibility of the agricultural departments, and advice and application forms may be obtained from the appropriate MAFF Regional Service Centre in England, the SOAFD in Scotland or WOAD in Wales. Contact names and addresses and telephone numbers are given in Annex B. 2 For some specific activities which may occur in woodland the licensing authorities are the nature conservation agencies (EN, SNH, CCW). These activities are: · ’development’ as defined under the Town and Country Planning Acts and subsequent Statutory Instruments and Orders of 1990 (England and Wales) and 1972 (Scotland) which would damage setts or disturb badgers in them; this includes construction of forest roads, erecting buildings, quarrying and some forms of use such as motor sports and paintball games; · interfering with setts or disturbing badgers in setts for the purposes of killing foxes in order to protect released game or wildlife; (interfering with setts to kill foxes in order to protect livestock would require licensing by agricultural departments); · interfering with setts or disturbance of badgers in setts for the purpose of protecting, or to enable archaeological investigation of, scheduled ancient monuments; · interference for scientific, educational or conservation purposes; · interference for the purpose of investigating whether an offence has been committed. Contact names, addresses and telephone numbers for EN, SNH and CCW are given in Annex B. The Protection of Badgers Act 1992 is new legislation and it will take some time before court cases establish legal precedents which will allow more precise interpretation of terms such as “disturbance” and “interference”. In the meantime, licensing authorities have to use their judgement on which activities require a licence and which do not. At the outset this can only be done on a case by case basis, but licensing authorities have said that they intend to adopt a common sense approach. 3 FOREST OPERATIONS AND BADGER SETTS M ANAGEMENT GUIDELINES General ost forestry operations can be carried out without Minterference to badger setts, provided they are carefully planned and supervised. These guidelines are designed to minimise interference to badger setts during forestry operations and therefore reduce the number of occasions on which a licence will be needed. They summarise the procedures and practices which are likely to be judged as ‘reasonable’ precautions to avoid damage or disturbance in most circumstances. Licences will still be required however in cases where a forestry operation would be expected to interfere with a badger sett as defined in the Act despite the use of the guidelines; or where the guidelines cannot be adopted. Each application for a licence will be looked at on its merits and licences will not be issued “just in case” or as a form of insurance against subsequent interference. Whenever there is any doubt about whether a licence is needed, advice should be sought from the appropriate licensing authority. (See APPLYING FOR A LICENCE, page 14). Locating and Recording Setts nformation on the location of badger setts should be gleaned from I all available sources including forest rangers, local badger groups and conservation organisations, landowners and gamekeepers. All setts should be recorded on maps at an appropriate scale (normally 1:10,000 or larger). In areas where deliberate illegal disturbance of badgers is a risk such maps may need to be kept confidential, but they should always be available to operational managers. Setts records should be included or referred to in forest conservation plans. Badger populations fluctuate and individual animals move from sett to sett. Over a period of years new setts are created and others fall into disuse. Some setts are used only at specific seasons. When forest operations are planned therefore it is essential that a check should be made for the presence and extent of any badger setts in the area concerned, especially before cultivation, civil engineering or tree-felling operations. Badger setts within thicket and pole-stage stands of trees which have not yet been thinned can easily be overlooked. 4 Badgers are social animals living in groups of about five to twelve. Usually a group has more than one sett in its territory and setts vary in their status and level of use so that four main types of sett can be identified, although the distinctions between are not always clear. a. Main setts are the largest and most important; each group usually has only one main sett which is normally in continuous use and is the breeding sett. Characteristic features are: · several holes (average over Britain is twelve but exceptionally it can be as few as one) with large spoil and bedding heaps at the entrance; · signs of usage throughout the year; · well worn paths to and from the sett and between entrances. b. Annexe setts are often found close to main setts, usually under 150 metres away, have several holes (average eight) and are connected to the main sett by well worn paths.They may not be in continuous use. c. Subsidiary setts are similar to annexe setts, but are usually smaller (average of four holes), do not have obvious connecting paths and are not permanently in use. They are at least 50 metres from the main sett. d. Outlying setts can be found well away from main setts and with no path to other setts. They are used sporadically by badgers but may be used by foxes or rabbits at other times. The average number of holes is two. blocked entrances entrances bedding material 0 5m Plan of a badger sett. Main setts can become a complex labyrinth. 5 FOREST OPERATIONS AND BADGER SETTS Identifying Setts in Current Use by Badgers a. The shape of the tunnel, not the entrance hole itself, is a rounded or flattened oval (broader than high) with diameter of at least 25 cm. b. Badger footprints, clawmarks and soil smoothed by the passage of badgers may be present near the entrance.